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2016
2016
Environmental Toxicology Program
Bureau of Environmental Health
Massachusetts Department of Public Health
250 Washington Street
Boston, MA 02108
Email: [email protected]
Phone: (617) 624-5757
Massachusetts Beach Testing Results: Annual Report
Good Harbor Beach, Gloucester, MA
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2016
Executive Summary
Swimming at Massachusetts beaches is one of the most popular recreational activities in the state, with over
111 million individual trips to one of the 1,100 beaches each year (EOEEA, 2007; EOHED, 2016). As good water
quality is essential to having a safe and enjoyable beach visit, it is critical to both monitor the water quality and
immediately notify the public of any potential water quality concerns. Each year, the Environmental Toxicology
Program in the Massachusetts Department of Public Health (MDPH), Bureau of Environmental Health collects
water quality information from local health departments as well as the Massachusetts Department of
Conservation and Recreation. This report provides a description of this information and is summarized
immediately below.
Water quality: In 2016, a total of 15,604 water samples were collected from 586 marine and 594
freshwater beach sampling locations. These locations represent 529 marine and 549 freshwater
beaches. All marine beach communities and 99% of freshwater communities reported water quality
information to MDPH. Approximately 3.5% and 3.0% of the samples exceeded the Massachusetts water
quality standards (based on bacteria) for marine and freshwater beaches, respectively. The overall low
exceedance rates indicate that Massachusetts beaches have generally high water quality. Elevated
bacteria accounted for 63% of poor water quality notifications (i.e., beach postings); other reasons for
notifications included harmful algae (cyanobacteria) blooms, rainfall (typically associated with elevated
bacteria), and other hazards (e.g., strong currents, shark sightings).
Field data: In 2016, a majority of water samples (approximately 93%) submitted to MDPH had
accompanying field data. Rainfall and local pollution sources at sampling sites were identified as two
important factors that contributed to elevated bacteria levels at recreational waterbodies. Generally,
the number of exceedances dropped exponentially as the days since rainfall increased. Among those
samples collected near potential pollution sources, the exceedance rate was higher than those without a
potential pollution source.
Public notification: The MDPH marine beaches website (http://ma.healthinspections.us/public_21/)
provides near real-time information on bacteria levels at public marine beaches, as well as information
on historic bacteria levels. MDPH initiated usage analyses of its beaches website in 2016 by recording
the number of unique visitors. The number of website users was highest in July and August, which
corresponded with the height of the beach season in Massachusetts. Individuals were also notified of
unsafe conditions at beaches through the use of physical signage that is required to be posted by beach
operators. All marine and 74% of freshwater beaches were in compliance with the public notification
requirement. The 100% marine compliance is a first since the passage of the Massachusetts Beach Act.
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2016
Introduction
Swimming-associated health risks have been documented
in numerous studies (Marion et al., 2010; Wade et al.,
2003). Beachgoers may be exposed to pathogens through
recreational activities in and around polluted waterbodies
(Hlavsa et al., 2015). In the United States, most
swimming-associated diseases are caused by a variety of
pathogens associated with fecal contamination (Cabelli et
al., 1982; USEPA, 2012). Human fecal matter can enter
beach water in a variety of ways, including sewage
treatment system failures, combined sewer overflows,
discharge of sewage by boats, re-suspension of
sediments, and rainfall and resulting surface runoff (Galfi
et al., 2016; Rodrigues et al., 2016).
To address concerns over swimming-associated illness,
improve public health for beachgoers, and notify the
public about the quality of beach water, MDPH
regulations have required regular water quality
monitoring and public notification of unsafe conditions
since 2001. All public and semi-public bathing beaches in
Massachusetts are monitored for fecal indicator bacteria
(FIB), and on occasion harmful algae during the beach
season which generally begins when the school year
finishes in mid-June and ends during the weekend of
Labor Day.
MDPH adopted the USEPA criteria for enterococci and
E. coli in marine and freshwater. These criteria consist of
both a single sample and geometric mean (geomean)
value reported as colony forming units per 100 milliliter
of water (CFU/100mL) (see Table). When beach water
does not meet these water quality standards, MDPH
requires that the beach be posted with a notice alerting
the public to the possible risk of swimming. At a majority
of beaches in Massachusetts, water quality is considered
to be unacceptable when two samples collected on
consecutive days exceed the water quality standards.
Beaches with a history of multi-day elevated bacteria
levels are required to post after a single exceedance.
Posting is also required when the geomean of the five
most recent non-rainfall impacted samples exceeds the
geomean standard.
Table. MDPH recreational water quality criteria (CFU/100 mL)
In addition to water samples, field data such as days since
rainfall and potential pollution sources are required to be
collected at the time of sample collection. Field data help
facilitate the interpretation of bacteria data and can
improve the understanding of water quality at the local
and state level.
Spring Brook Park Beach, Bedford, MA
Beach
Type Indicator
Single
Sample Geomean
Marine Enterococci >104 >35
Freshwater Enterococci >61 >33
E. coli >235 >126
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2016
Water Quality
Marine beach exceedances. During the 2016 beach
season, a total of 7,904 samples were collected and
analyzed from 586 marine beaches. Of these 586
beaches, 140 (24%) in the 60 communities with beaches
had at least one bacterial exceedance (see Figure 1). A
total of 274 out of the 7,904 samples exceeded the 104
CFU/100 mL standard. The percentage of exceedances for
marine waters in 2016 was 3.5%, which was much lower
than the historical average exceedance rate of 4.9%. The
number of marine beach exceedances in each community
during 2016 is shown in Figure 1. The marine beaches in
Boston, Lynn, and Quincy had the highest number of
exceedances in 2016.
Freshwater beach exceedances. During the 2016 beach
season, 7,700 samples from 594 freshwater beaches
were collected and analyzed for the approved FIB (i.e. E.
coli or enterococci). Most freshwater beaches (87%) used
E. coli. Among the 594 freshwater beaches, 115 (19%) in
180 communities reporting beach data had at least one
bacterial exceedance (Figure 2). A total of 232 out of the
7,904 samples exceeded the standard. The percentage of
exceedances for freshwater in 2016 was 3.0%, which was
much lower than the historical average exceedance rate
of 3.8%. The number of freshwater beach exceedances in
each community during 2016 is shown in Figure 2. The
number of exceedances in freshwater beaches in 2016
varied among communities, with the highest number in
Brimfield, Templeton, and West Tisbury.
Posting beaches. During the 2016 beach season, poor
water quality and/or unsafe conditions required the
postings of beaches on 274 occasions. These postings
advised individuals not to swim or bathe in the water.
Figure 3 displays the causes of postings in 2016. The
majority of postings were due to the exceedance or
expected exceedance (i.e., rainfall) of water quality
standards. For marine beaches, there were 160 postings
due to elevated bacteria, rainfall, or other (e.g., rip
current, shark sightings). For freshwater beaches, there
were 114 postings due to elevated bacteria, rainfall, and
harmful algae blooms.
Figure 3. Posting details for marine and freshwater beaches in 2016
Figure 1. Marine beach water quality exceedances in 2016
Figure 2. Freshwater beach water quality exceedances in 2016
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2016
Field Data Potential pollution sources. The presence of pollution
sources at beaches was associated with a higher risk of
bacterial exceedances. Figure 4 shows that the
exceedance rate of samples which noted the presence of
specific pollution sources is higher than those without the
presence of any pollution source regardless of beach
type. It is worth mentioning that when pollution source
information was not reported (i.e., unknown) in the field
data, the exceedance rate of water samples was even
higher than those with the presence of a specific
pollution source. Without pollution source information,
the ability to evaluate the potential impacts on water
quality is diminished.
Figure 4. Exceedance rate of water samples associated with the presence, absence, or none reporting of environmental pollution sources at beaches in Massachusetts in 2016
Unknown: no information provided; yes: specific pollution source observed; no: no pollution source observed.
Rainfall. Rainfall is recognized as one of the major drivers
of bacterial exceedances in beach water (Harder-
Lauridsen et al., 2013). An exponential drop in the
number of exceedances occurs as the time between
rainfall and sample collection increases (Figure 5). For
marine beaches, 158 of 274 bacterial exceedances
occurred within 24 hours after a rain event; for
freshwater, 126 of 230 exceedances were observed
within 48 hours after a rain event.
Figure 5. Relationship between the number of bacterial exceedances and days since rainfall in 2016
The historical relationship between exceedances of water
quality criteria at marine and freshwater beaches and the
total amount of rainfall between June and August is
shown in Figure 6. The rainfall data were obtained from
the National Oceanic and Atmospheric Administration
(NOAA, 2016). Rainfall data sets from Boston and
Chatham were used to represent monthly rainfall
amounts at marine beaches; data sets from Amherst and
Ashburnham, along with those from Boston and Chatham
were used to represent amounts at freshwater beaches.
For both marine and freshwater beaches, exceedances
generally rise and fall with rainfall amounts, with some
exceptions. In 2016, Massachusetts received the least
amount of rain during any beach season since 2001. The
low rainfall amount is likely a primary reason for the low
exceedance rates in 2016.
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UnknownYesNo
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Days since rainfall
Marine
Freshwater
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2016
Figure 6. The historical relationship between rainfall amounts and exceedance rates at (A) marine and (B) freshwater beaches in Massachusetts from the 2001 to 2016 beach seasons
Public Notification
Beach website. The MDPH beach monitoring website
(http://ma.healthinspections.us/public_21/) provides the
public with the most up-to-date marine beach testing and
posting information and presents the data in an easy-to-
use format. Overall, over 4,000 users visited the website
during the season (this includes both new and returning
users). An analysis of weekly usage data demonstrated
an increase in the number of users as the beach season
progressed and consistent usage during the second half
of the season (Figure 6). The number of website users
(n=398) peaked during week 9, which corresponds with
late July. The second busiest week was that which
included July 4th (week 6), when 364 people visited the
site.
Beach postings. When water quality standards are
exceeded or other safety concerns warrant, beach
operators are required to post signage at the beach
advising individuals of the hazard and recommending
they stay out of the water. This is an essential part of the
public notification system. Marine and freshwater
beaches were posted properly 100% and 75% of the time,
respectively.
Figure 7. Number of MDPH marine beach website users per week during the 2016 beach season
Conclusions
In 2016, the exceedance rates at marine and freshwater
beaches were lower than historical averages. Rainfall is a
significant driver of bacteria exceedances, and the low
rainfall amount received throughout the beach season
across the state is likely a primary factor for the low
exceedance rates. However, given the number of beaches
sampled in Massachusetts, the average historical
exceedance rates of less than 5% indicate that
Massachusetts has beaches with generally high water
quality. Public notification of marine results and postings
via MDPH’s monitoring website continued to be an
effective means of communicating with the public.
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2016
Acknowledgements
This work was partially supported by a U.S. EPA Beaches Environmental Assessment and Coastal Health (BEACH) grant and a U.S. Centers for Disease Control and Prevention’s Preventive Health and Health Services grant. MDPH received assistance from local, regional, and state partners, including Massachusetts boards of health, regional health networks, and the Massachusetts Department of Conservation and Recreation, in ensuring that bathing beaches were tested and data were submitted appropriately.
References
Cabelli, V.J., Dufour, A.P., McCabe, L.J., Levin, M.A. 1982.
Swimming-associated gastroenteritis and water quality.
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Executive Office of Housing and Economic Development
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Galfi, H., Österlund, H., Marsalek, J., Viklander, M. 2016.
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Rodrigues, V.F.V., Rivera, I.N.G., Lim, K.-Y., Jiang, S.C.
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2016
For more information, please visit:
MDPH Beaches and Algae website: http://www.mass.gov/dph/beaches
MDPH Marine Beach website: http://ma.healthinspections.us/public_21/
Or contact:
Environmental Toxicology Program
Bureau of Environmental Health
Massachusetts Department of Public Health
250 Washington Street
Boston, MA 02108
Email: [email protected]
Phone: (617) 624-5757
Fax: (617) 624-5813
South Beach, Edgartown, MA